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Energy Degradation and Ecosystem Development: Theoretical Framing, Indicators

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Energy Degradation and Ecosystem Development: Theoretical Framing, Indicators Ecological Indicators 20 (2012) 204–212 Contents lists available at SciVerse ScienceDirect Ecological Indicators jo urnal homepage: www.elsevier.com/locate/ecolind Energy degradation and ecosystem development: Theoretical framing, indicators definition and application to a test case study ∗ Alessandro Ludovisi Dipartimento di Biologia Cellulare e Ambientale, Università di Perugia, Via Elce di Sotto, 06123 Perugia, Italy a r t i c l e i n f o a b s t r a c t Article history: During the last few decades, the so-called “maximum dissipation principle” has raised a wide debate as Received 21 May 2011 a paradigm governing the development of ecological systems. In the present contribution, after having Received in revised form 5 February 2012 discussed the meaning of the term energy degradation within the framework provided by the entropy Accepted 9 February 2012 and the exergy balance, it is suggested to distinguish three different facets of the phenomenon of the energy degradation, respectively dealing with the overall, system and environmental degradation. In Keywords: relation with ecological indication, the above classification shows that different types of indicators of Ecological indicators energy degradation can be defined, thus emphasising that a clear reference to the specific facet consid- Ecological orientors Entropy ered should be made in order to avoid ambiguous statements. The behaviour of several thermodynamic Exergy indicators, which include previously derived indices and a new set of entropy-based indicators, is exam- Lake Trasimeno ined along the seasonal progression in a lake ecosystem, and the effectiveness of the considered indicators in characterising the development state is evaluated by comparing their responses with the main succes- sional traits of the phytoplankton community. The results show that, although overall degradation and related indices may deserve consideration as indicators of the extent of the degradative (biotic and abi- otic) processes acting within an ecosystem, their significance as indicators of development state appears to be limited. On the other hand, indicators related to environmental degradation appear to be more promising as indicators of the development state, provided that some methodological issues dealing with the effect of the abiotic noise are properly addressed. The net radiative entropy exchange shows a significant correlation with phytoplankton successional traits, thus suggesting that the entropy changes in the radiative portion of the entropy budget are the most informative in relation to the development state of aquatic communities. The methodology adopted also lends itself to be used for evaluating the energy quality associated with an energy flow, which is here measured by the energy-to-entropy ratio. © 2012 Elsevier Ltd. All rights reserved. 1. Introduction energy degradation. Although the authors explicitly avoided to formulate the principle in terms of entropy, it is rooted on the During the last century, many efforts were made to identify second law of thermodynamics and supported by the theoretical thermodynamic-based functions possessing specific realisations framework that has inspired the formulation of several “maxi- towards which ecosystem development is supposed to be ori- mum entropy production principles” (MEPP) in different fields (see ented, the so-called orientors (see reviews in: Müller and Leupelt, a historical review in Martyushev and Seleznev, 2006), including 1 1998; Fath et al., 2001; Jørgensen and Svirezhev, 2004; Müller, ecology (Ulanowicz and Hannon, 1987; Kleidon and Lorenz, 2005). 2005; Jørgensen et al., 2007). Among them, the so-called “maxi- In their paper, Schneider and Kay start distinguishing between mum dissipation principle”, stemming from the work of Schneider energy dissipation and energy degradation, concepts that have and Kay (1994), has received wide attention, as well as serious been indifferently used to denote the loss of the work-potential criticisms (see, e.g., Straskrabaˇ et al., 1999; Jørgensen et al., 2000; of energy since the appearance of the earlier statements of Nielsen, 2000; Fath et al., 2001, 2004; Pykh, 2002; Müller et al., the second law of thermodynamics (see, e.g., Brunhes, 1908). 2006; Meysman and Bruers, 2010). In short, the principle states that ecosystems tend to maximise the dissipation of the incom- ing energy and develop structural and functional attributes to abet 1 The relationship between MEPP and Prigogine’s minimum entropy production principle (Prigogine, 1945) has been the subject of long-standing discussions (see, e.g., Jaynes, 1980 and Martyushev and Seleznev, 2006). These principles should not ∗ Corresponding author. Tel.: +39 075 585 5707; fax: +39 075 585 5733. be mutually opposed since they are applicable to different stages of the evolution E-mail addresses: [email protected], [email protected] of a nonequilibrium system (Nicolis and Prigogine, 1977). 1470-160X/$ – see front matter © 2012 Elsevier Ltd. All rights reserved. doi:10.1016/j.ecolind.2012.02.019 A. Ludovisi / Ecological Indicators 20 (2012) 204–212 205 According to Schneider and Kay, dissipation of energy “means to higher values of SED with respect to crop fields and perturbed areas, move energy through the system”, thereby reflecting the ability of a but some inconclusive or contradictory results also emerged (e.g. system to discharge the absorbed energy towards the environment. Kutsch et al., 2001). Technical limitations related to the low accu- As shown by the authors by making reference to the Bénard exper- racy of the available remote sensing data or calibration issues might iment (Bénard, 1900), the heat transfer rate in a heated container help to explain some of the inconclusive results obtained (Dewulf enclosing a fluid increases linearly as a function of the imposed et al., 2008). Kutsch et al. (2001) claim that the energy exchanges temperature gradient, but the heat transfer becomes faster when due to abiotic phenomena (the abiotic noise), with a particular ref- convective cells (the Bénard Cells) spontaneously appear within the erence to the sensible heat losses, significantly obfuscates the biotic fluid. This simple phenomenon demonstrates that self-organised signal. structures can emerge in systems subjected to an energy flow, and However, a part of the limitations of SED resides on the fact also that the organisation makes the system more efficient in dis- that it simply expresses the fraction of the absorbed solar radiation sipating the absorbed energy. On the other hand, Schneider and that is converted into non-radiative energy losses. Therefore, the Kay defines energy degradation in terms of loss of work potential significance of SED as an indicator of energy degradation relies on of energy, i.e., in terms of exergy loss (Evans et al., 1966), stating the hypotheses that non-radiative releases are the most significant that “degradation of energy means to destroy the ability of energy ones in terms of degradation, or that the longwave budget is negli- to produce gradients that can accomplish work” and that “energy gible, which are both questionable assumptions. More importantly, degradation means exergy destruction”. In the Bénard experiment, SED has the drawback of being based on the energy budget terms the appearance of the convective cells reduces the extent of the of an ecosystem, and, as such, it is unable to account properly for overall temperature gradient within the fluid and increases entropy the change in energy quality, because no measure of energy quality production and exergy destruction. The fact that energy dissipation is associated with incoming and outgoing energy flows. and exergy destruction do not follow the same trend, the latter In the attempt to take into account the drop of energy qual- increasing more than linearly with respect to the temperature gra- ity due to dissipative processes, Svirezhev and Steinborn (2001) dient, corroborated the idea that they account for different aspects derived a method of calculation for the radiation exergy flux across of the dissipative process. an ecosystem (Exf), by following a information-statistical approach: As a whole, the Bénard experiment was used by Schneider and Eout out out l out Es Kay to support the “restated second law”, according to which any Ex f = E ln + Es ln + Rn (2) l Ein Ein system moved away from equilibrium will utilise all avenues avail- l s able to counteract the imposed gradient. In order to comply with where E represents the energy flow associated with longwave (sub- the principle, a sequence of states of increasing complexity (includ- script l) or shortwave (subscript s) radiation incoming (superscript ing chaotic structures) must be expected as the applied gradient in) or outgoing (superscript out) from the system surface. Together increases, with each transition being accompanied by an increas- in in Á with Exf, the authors proposed the ratios R = Rn/(El + Es ) (the ing ability to destroy gradients and degrade energy. By following in in Á radiation efficiency coefficient) and Ex = Exf/(El + Es ) (the exergy a heuristic inductive approach, Schneider and Kay extended the efficiency coefficient) as useful indicators of the efficiency of the above principle to living systems, suggesting that “life exists on “radiative machine” working at the ecosystem surface. In compar- earth as another means of dissipating the solar induced gradient ing the seasonal trends of these indicators in a crop field and a and, as such, is a manifestation
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